EP0976718A2 - Improved nitration process - Google Patents
Improved nitration process Download PDFInfo
- Publication number
- EP0976718A2 EP0976718A2 EP99114369A EP99114369A EP0976718A2 EP 0976718 A2 EP0976718 A2 EP 0976718A2 EP 99114369 A EP99114369 A EP 99114369A EP 99114369 A EP99114369 A EP 99114369A EP 0976718 A2 EP0976718 A2 EP 0976718A2
- Authority
- EP
- European Patent Office
- Prior art keywords
- gases
- aromatic compound
- nitric acid
- nitrator
- nitratable
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
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Classifications
-
- C—CHEMISTRY; METALLURGY
- C07—ORGANIC CHEMISTRY
- C07C—ACYCLIC OR CARBOCYCLIC COMPOUNDS
- C07C201/00—Preparation of esters of nitric or nitrous acid or of compounds containing nitro or nitroso groups bound to a carbon skeleton
- C07C201/06—Preparation of nitro compounds
- C07C201/08—Preparation of nitro compounds by substitution of hydrogen atoms by nitro groups
Definitions
- This invention relates to an improved continuous process for the nitration of nitratable organic compounds and particularly for the preparation of mononitrobenzene (MNB) from benzene utilizing nitric acid and sulfuric acid feed stocks.
- MNB mononitrobenzene
- nitrous oxide (NO x ) gases produced in the nitration process are collected in water under pressure to produce weak nitric acid which is recycled to the nitric acid feed stock.
- Nitrated aromatic hydrocarbons and nitrated halogenated aromatic hydrocarbons and particularly mononitrobenzene are important chemical intermediates.
- Guenkel et al, United States Patent No. 5,313,009 (the '009 patent), assigned to the assignee of the present invention describes a continuous process to nitrate a nitratable aromatic compound, typically an aromatic hydrocarbon or a halogenated aromatic hydrocarbon, and particularly benzene, in which the formation of oxidation by-products is substantially reduced compared with the prior art and wherein the reaction rate is substantially increased.
- a nitratable aromatic compound typically an aromatic hydrocarbon or a halogenated aromatic hydrocarbon, and particularly benzene
- NO x gases are still formed which preferably are not released into the atmosphere for environmental reasons.
- the prior art has suggested treating these NO x gases with a caustic solution to form sodium nitrite or sodium nitrate salts, which are disposed of as the salt.
- Small quantities of CO 2 are also formed in the nitration process. CO 2 will react with sodium hydroxide to form sodium carbonate; this increases the consumption of sodium hydroxide.
- the use of sodium hydroxide and formation of salts which must be subsequently disposed of is not completely acceptable on an industrial basis.
- the discharge of nitrates and especially nitrites of sodium is facing increasingly strict regulation.
- the present invention describes a system for removal of NO x gases which can be utilized in conjunction with the nitration process disclosed in the aforesaid '009 patent, as well as other nitration processes where NO x gases are formed to efficiently and effectively convert the NO x gases into weak nitric acid, preferably recycled to the nitric acid feed stock.
- the present invention provides a continuous nitration process of an aromatic compound such as benzene utilizing nitric acid and sulfuric acid feed stocks wherein NO x gases produced in the process are contacted with water under pressure and converted to weak nitric acid which is recycled to the nitric acid feed stock.
- NO x gases are collected from strategic areas of the nitrating system, contacted with air and water, for example, in a packed bed unit at elevated temperature and pressure whereby the NO x gases are absorbed by the water to form weak nitric acid.
- the weak nitric acid is recovered from the packed bed unit and recycled to the nitric acid feed stock.
- CO 2 is not absorbed in a NO x scrubber if the scrubber is operated in an acidic mode. Clean NO x free vent gas is vented from the packed bed unit.
- the system is not only effective and efficient, but additionally is cost saving in that the NO x gases being recovered as nitric acid are reused in the nitration process.
- a pipe nitrator 100 receives concentrated sulfuric acid from conduit 102, nitric acid from conduit 104 and hydrocarbon, i.e., benzene, to be nitrated from conduit 106.
- the acid streams are blended in a ratio such that the resulting mixed acid contains nitric acid mostly in the form of reactive species, i.e., the nitronium ion as described in the '009 patent.
- the two acid streams from conduits 102 and 104 may be mixed in line before entering the pipe nitrator 100 or they may be introduced separately into the pipe nitrator 100.
- the pipe nitrator 100 discharges to a stirred tank type nitrator 112.
- the reaction rate is very fast, which is specific to the hydrocarbon species to be nitrated and specific to the operating conditions, the reaction may go essentially to completion inside the pipe nitrator 100 so that the stirred tank type of nitrator 112 is not required.
- the pipe nitrator 100 serves mainly as a hydrocarbon dispersion device. Fresh nitrating acid enters the stirred tank nitrator 112 and intimately mixes with fresh hydrocarbon.
- the process fluids pass to a separator 114 and the nitro product compound is discharged from separator 114 through conduit 116 and fed to a product wash and effluent treatment system 124.
- Pure nitro organic product i.e., mononitrobenzene when benzene is treated, is recovered at conduit 125, aqueous effluent is discharged through conduit 126 and some organic recycle is fed by line 127 to hydrocarbon feed 106.
- Spent sulfuric acid recovered from separator 114 is delivered to a sulfuric acid concentrator 118.
- water is removed via conduit 120 which is fed to a vacuum system 123 while reconcentrated sulfuric acid is recycled to the pipe nitrator 100 through conduit 117.
- NO x gases are drawn off in vacuum system 123 and collected through line 128 at head unit 121. Condensate from vacuum system 123 is fed to product wash and effluent treatment system 124 where additional NO x gases are drawn off and fed to head unit 121 through a second line 128. Finally, additional NO x gases are vented from separator 114 and collected at head unit 121 through a third line 128. All of the NO x gaseous process vent streams 128, after being combined at head unit 121, are fed to conduit 129 for mixing with air with this mixed stream being fed to a packed bed unit 130 for contact with water 131 to form dilute or weak nitric acid. The weak nitric acid is recycled through line 132 to nitric acid feed stock line 104. Clean NO x free vent gas is vented from the packed bed through line 134.
- the NO x abatement/acid production unit 130 is shown as two separate packed bed sections 30 and 40.
- the lower packed bed section 30 receives the NO x gases mixed with air through line 129 and water 131.
- the NO x gases, water and air at a pressure of 2 to 5 atmospheres are circulated through packed bed 30 and recovered as weak nitric acid at 132 which is recycled and used as nitric acid stock.
- This unit will recover approximately 98% of the NO x gases as weak nitric acid in unit 30.
- Increased pressure favors increased recovery.
- a heat exchanger generally at 32 on unit 30 maintains the temperature in unit 30 as low as possible favoring acid production.
- the second or upper section 40 is used for clean up of the tail gases from first section 30.
- the second section is a shorter section and is irrigated either with circulating water or caustic.
- caustic is not used in that it will be consumed by CO 2 .
- This section receives NO x tail gases from section 30 at conduit 32 and removes residual NO x gases to give a colorless stack gas discharged at 42.
- the second bed may be either eliminated or, if it is operated with water, may feed to the first bed.
- the liquid effluent is combined with other weak processing effluents for recycling through line 132.
- the packed bed sections are operated at pressures which vary from 2 to 5 atmospheres as above stated. Typically, the weak nitric acid formed for recycling will vary in strength from 2 to 10 weight percent, depending upon the requirements of the process.
- the NO x collection will be carried out at the temperature and pressure of the nitrating process.
- the pressure in the unit for forming dilute nitric acid will preferably be at an elevated pressure selected to accommodate most efficient formation of nitric acid under the other conditions of the nitrating process.
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
- Treating Waste Gases (AREA)
- Glass Compositions (AREA)
- Processing Of Solid Wastes (AREA)
- Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)
Abstract
Description
- FIGURE 1 diagrammatically illustrates a continuous nitrating process carried out in the adiabatic mode, as described in the '009 patent, utilizing the NOx recovery system of the present invention, and
- FIGURE 2 illustrates two separate but interconnected packed bed sections utilized in contacting the NOx gases with water to form and concentrate nitric acid for recycling.
Claims (8)
- A continuous process to nitrate a nitratable aromatic compound comprising:a) introducing a nitratable aromatic compound, nitric acid and sulfuric acid into a nitrator;b) reacting said nitratable aromatic compound, nitric acid and sulfuric acid under controlled conditions to produce a nitrated aromatic compound and NOx gases;c) separating said NOx gases from said nitrated aromatic compound;d) contacting said NOx gases with water under pressure to form weak nitric acid, ande) recycling said nitric acid for reuse in the process.
- The process of claim 1 wherein said nitratable aromatic compound is benzene and the nitrated aromatic compound is mononitrobenzene.
- The process of claim 2 wherein said NOx gases are contacted with water under pressure in a packed bed system.
- The process of claim 3 wherein said packed bed system comprises two separate but connected packed beds.
- A nitration system comprising a nitrator for nitrating a nitratable aromatic compound, including feed means for feeding each of a nitratable aromatic compound, nitric acid feed stock and sulfuric acid feed stock into said nitrator; separator means for separating a nitrated aromatic compound from spent sulfuric acid; means for separating NOx gases from said nitrated aromatic compound, and means for contacting said NOx gases with water to form weak nitric acid.
- The nitration system of claim 5 wherein said nitratable aromatic compound is benzene.
- The nitration system of claim 6 wherein said nitrator further includes a product wash and effluent system and means for separating and collecting NOx gases therefrom.
- The nitration system of claim 7 wherein said nitrator further includes a vacuum system for receiving nitrated aromatic compound and water and means for separating and collecting NOx gases therefrom.
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| US126087 | 1987-11-30 | ||
| US09/126,087 US5963878A (en) | 1998-07-30 | 1998-07-30 | Nitration process |
Publications (3)
| Publication Number | Publication Date |
|---|---|
| EP0976718A2 true EP0976718A2 (en) | 2000-02-02 |
| EP0976718A3 EP0976718A3 (en) | 2000-12-27 |
| EP0976718B1 EP0976718B1 (en) | 2003-03-12 |
Family
ID=22422927
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| EP99114369A Expired - Lifetime EP0976718B1 (en) | 1998-07-30 | 1999-07-21 | Improved nitration process |
Country Status (4)
| Country | Link |
|---|---|
| US (1) | US5963878A (en) |
| EP (1) | EP0976718B1 (en) |
| AT (1) | ATE234272T1 (en) |
| DE (1) | DE69905811T2 (en) |
Cited By (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2012160072A1 (en) | 2011-05-24 | 2012-11-29 | Basf Se | Process for preparing polyisocyanates from biomass |
| WO2014016289A1 (en) | 2012-07-27 | 2014-01-30 | Bayer Materialscience Ag | Method for producing nitrobenzene by adiabatic nitriding |
| US8697913B2 (en) | 2009-06-17 | 2014-04-15 | Huntsman International Llc | Chemical installation |
| US8933262B2 (en) | 2011-05-24 | 2015-01-13 | Basf Se | Process for preparing polyisocyanates from biomass |
| US9260377B2 (en) | 2012-07-27 | 2016-02-16 | Bayer Materialscience Ag | Method for producing nitrobenzene by adiabatic nitriding |
| US9284256B2 (en) | 2012-07-27 | 2016-03-15 | Bayer Materialscience Ag | Process for the production of nitrobenzene by adiabatic nitration |
| WO2020212333A1 (en) | 2019-04-17 | 2020-10-22 | Covestro Deutschland Ag | Process for the continuous production of nitrobenzene |
| WO2020212334A1 (en) | 2019-04-17 | 2020-10-22 | Covestro Deutschland Ag | Process and device for producing nitrobenzene |
Families Citing this family (11)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP4485731B2 (en) | 2000-03-02 | 2010-06-23 | ダウ グローバル テクノロジーズ インコーポレイティド | Tubular reactor, process for conducting liquid / liquid multiphase reaction in tubular reactor and process for ring nitration of aromatic compounds in tubular reactor |
| JP3635026B2 (en) * | 2000-06-14 | 2005-03-30 | 株式会社サンテックシステム | Sulfuric acid recycling equipment |
| DE10047163A1 (en) * | 2000-09-22 | 2002-04-11 | Basf Ag | Process for the nitration of aromatic hydrocarbons |
| SG119142A1 (en) * | 2000-11-21 | 2006-02-28 | Suntec System Co Ltd | Sulfuric acid recycle apparatus |
| US9227909B2 (en) | 2012-10-10 | 2016-01-05 | Covestro Deutschland Ag | Method for the continuous production of nitrobenzene |
| WO2016050759A1 (en) | 2014-10-02 | 2016-04-07 | Covestro Deutschland Ag | Exhaust gas cleaning in a method for continuously producing dinitrotoluene |
| DE102017110084B4 (en) | 2017-02-03 | 2019-07-04 | Josef Meissner Gmbh & Co. Kg | Process and plant for the adiabatic nitration of aromatics |
| DE102018217955B4 (en) * | 2018-10-19 | 2020-06-04 | Plinke Gmbh | Process for working up mixed acid and waste water from the nitration of aromatics and device for carrying out the process |
| CN110511146A (en) * | 2019-09-17 | 2019-11-29 | 四川北方红光特种化工有限公司 | The production method and its production system of a kind of low single nitro ortho-xylene of waste acid quantity |
| EP4648884A1 (en) | 2023-01-09 | 2025-11-19 | Basf Se | Process for removing nitric oxide, nitrous oxide and carbon monoxide from a gas stream |
| WO2025125207A1 (en) | 2023-12-11 | 2025-06-19 | Basf Se | Process for removing nitrogen monoxide, nitrogen dioxide and nitrous oxide from an exhaust gas stream |
Family Cites Families (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| FR2453846A1 (en) * | 1979-04-10 | 1980-11-07 | Azote & Prod Chim | PROCESS AND PLANT FOR MANUFACTURING NITROPARAFFINS BY NITRATION OF HYDROCARBONS IN THE GASEOUS PHASE |
| DE2921487C2 (en) * | 1979-05-26 | 1984-11-08 | Josef Meissner GmbH & Co, 5000 Köln | Process for the removal of volatile aromatic compounds |
| DE19512114C2 (en) * | 1995-04-04 | 2000-04-27 | Meissner Gmbh & Co Kg Josef | Recovery of nitric acid from nitriding processes |
-
1998
- 1998-07-30 US US09/126,087 patent/US5963878A/en not_active Expired - Lifetime
-
1999
- 1999-07-21 DE DE69905811T patent/DE69905811T2/en not_active Expired - Lifetime
- 1999-07-21 EP EP99114369A patent/EP0976718B1/en not_active Expired - Lifetime
- 1999-07-21 AT AT99114369T patent/ATE234272T1/en not_active IP Right Cessation
Cited By (10)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US8697913B2 (en) | 2009-06-17 | 2014-04-15 | Huntsman International Llc | Chemical installation |
| US9102586B2 (en) | 2009-06-17 | 2015-08-11 | Huntsman International Llc | Method for producing DADPM |
| WO2012160072A1 (en) | 2011-05-24 | 2012-11-29 | Basf Se | Process for preparing polyisocyanates from biomass |
| US8933262B2 (en) | 2011-05-24 | 2015-01-13 | Basf Se | Process for preparing polyisocyanates from biomass |
| WO2014016289A1 (en) | 2012-07-27 | 2014-01-30 | Bayer Materialscience Ag | Method for producing nitrobenzene by adiabatic nitriding |
| US9260377B2 (en) | 2012-07-27 | 2016-02-16 | Bayer Materialscience Ag | Method for producing nitrobenzene by adiabatic nitriding |
| US9284255B2 (en) | 2012-07-27 | 2016-03-15 | Bayer Materialscience Ag | Method for producing nitrobenzene by adiabatic nitriding |
| US9284256B2 (en) | 2012-07-27 | 2016-03-15 | Bayer Materialscience Ag | Process for the production of nitrobenzene by adiabatic nitration |
| WO2020212333A1 (en) | 2019-04-17 | 2020-10-22 | Covestro Deutschland Ag | Process for the continuous production of nitrobenzene |
| WO2020212334A1 (en) | 2019-04-17 | 2020-10-22 | Covestro Deutschland Ag | Process and device for producing nitrobenzene |
Also Published As
| Publication number | Publication date |
|---|---|
| DE69905811D1 (en) | 2003-04-17 |
| EP0976718A3 (en) | 2000-12-27 |
| EP0976718B1 (en) | 2003-03-12 |
| DE69905811T2 (en) | 2003-11-13 |
| US5963878A (en) | 1999-10-05 |
| ATE234272T1 (en) | 2003-03-15 |
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